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2,4,6-trinitrotoluene (TNT) - OEHHA

2,4,6-trinitrotoluene (TNT) - OEHHA

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1<br />

2,4,6-Trinitrotoluene (<strong>TNT</strong>)<br />

CAS No. 118-96-7<br />

Formula: C6H2(NO2) 3CH3 MW: 227.1<br />

Chemical Class: polynitroaromatic hydrocarbon<br />

Office of Environmental Health Hazard Assessment


2<br />

Use & Occurrence of <strong>TNT</strong><br />

• Explosives in military & industrial applications<br />

(munitions, coal/mineral mining, deep well/<br />

underwater blasting, building demolitions)<br />

• Chemical intermediate<br />

• In soil & surface/ground water near sites of use<br />

Office of Environmental Health Hazard Assessment


3<br />

Carcinogenicity Studies of <strong>TNT</strong><br />

• Studies in humans<br />

—One ecologic study<br />

—One case-control study<br />

—One cohort study<br />

—Several case reports<br />

• Studies in animals<br />

— Two-year dietary studies in rats of both sexes<br />

— Two-year dietary studies in mice of both sexes<br />

Office of Environmental Health Hazard Assessment


4<br />

Environmental <strong>TNT</strong> Contamination and<br />

Leukemia in Germany<br />

Ecologic incidence rates study (Kolb et al., 1993)<br />

• Apparent cluster of myeloid leukemia in city of Stadtallendorf<br />

confirmed<br />

— AML men RR 3.5 (CI 1.4-8.5) 6 cases in city, 28 in unexposed county<br />

— AML women RR 3.2 (CI 1.4-7.2) 7 cases in city, 29 in unexposed county<br />

— CML men RR 9.1 (CI 3.5-23.4) 7 cases in city, 13 in unexposed county<br />

— CML women RR 1.3 (CI 0.2-10.3) 1 case in city, 10 in unexposed county<br />

Population-based case-control study (Kilian et al., 2001)<br />

• Increased risk found for one neighborhood<br />

— All leukemia OR 5.1 (CI 1.1-23.8) 4 cases, 3 controls exposed<br />

— CML only OR 9.0 (CI 1.1-72.1) 3 cases, 1 control exposed<br />

Office of Environmental Health Hazard Assessment


5<br />

<strong>TNT</strong>-Exposed Munitions Workers and<br />

Liver Cancer in China<br />

Historical cohort study (Yan et al., 2002)<br />

• Incidence compared to non-exposed workers:<br />

RR 3.46 (p < 0.01)<br />

• Mortality compared to Chinese national rates for cities:<br />

RR = 2.71 (p


6<br />

Case Reports of Liver Cancer and<br />

Leukemia in Workers Exposed to <strong>TNT</strong><br />

• Liver Cancer<br />

— 1 case in Garfinkel et al. 1988<br />

— 9 cases in references cited by Yan et al. 2002<br />

• Liu 1986 (4 cases)<br />

• Wang 1991 (3 cases)<br />

• Yang and Xie 1995 (1 case)<br />

• Fu and Shang 1998 (1 case)<br />

• Leukemia<br />

— 2 cases in references cited by Yan et al. 2002<br />

• Wang 1991 (1 case)<br />

• Liu et al. 1995 (1 case)<br />

Office of Environmental Health Hazard Assessment


7<br />

Tumors in Female F344 Rats Fed <strong>TNT</strong><br />

for Two Years (Furedi et al., 1984a)<br />

Urinary<br />

bladder<br />

Lesions<br />

<strong>TNT</strong> dose (mg/kg/day)<br />

0.0 0.4 2.0 10.0 50.0<br />

Papilloma 0/54 0/54 0/55 1/55 5/55* #<br />

Carcinoma 0/54 0/54 0/55 0/55 12/55** #<br />

Papilloma &<br />

carcinoma<br />

0/54 0/54 0/55 1/55 17/55** #<br />

* p


8<br />

Tumors in Female B6C3F1 Mice Fed <strong>TNT</strong><br />

for Two Years (Furedi et al., 1984b)<br />

Lesions<br />

leukemia/ malignant<br />

lymphoma of the spleen<br />

<strong>TNT</strong> dose (mg/kg/day)<br />

0.0 1.5 10.0 70.0<br />

** p


9<br />

Summary of Carcinogenicity<br />

Studies in Rodents<br />

• Rare urinary bladder carcinomas and papillomas<br />

in female F344 rats<br />

• Leukemia & malignant lymphomas of the spleen<br />

in female B6C3F1 mice<br />

• No treatment related tumors observed in male<br />

rats or male mice<br />

Office of Environmental Health Hazard Assessment


10<br />

Other Relevant Data<br />

• Pharmacokinetics & Metabolism<br />

• Genotoxicity<br />

• Structure Activity Comparisons with<br />

Proposition 65 Carcinogens<br />

Office of Environmental Health Hazard Assessment


11<br />

Pharmacokinetics & Metabolism of <strong>TNT</strong><br />

• Absorption: GI tract, skin & lungs<br />

• Distribution: Primarily to the liver, kidneys,<br />

lungs & fat<br />

• Elimination: Primarily via urinary excretion<br />

• Metabolism:<br />

-Nitroreduction of aromatic nitro groups to<br />

hydroxylamino derivatives<br />

-Oxidation of methyl group to benzyl alcohol &<br />

benzoic acid derivatives<br />

Office of Environmental Health Hazard Assessment


12<br />

Metabolism<br />

The major metabolic<br />

pathways of <strong>TNT</strong><br />

(adapted from Bolt et<br />

al., 2006).<br />

Office of Environmental Health Hazard Assessment


13<br />

<strong>TNT</strong> Genotoxicity : Bacterial Systems<br />

Salmonella typhimurium Reverse Mutation Assays<br />

•Positive in strains TA98, TA1537, TA1538<br />

& TA100<br />

-Frameshift & basepair substitution<br />

-Presence or absence of metabolic activation<br />

-Requires nitro reductase, o-acetyltransferase<br />

Escherichia coli SOS Chromotest<br />

•Positive (human placenta microsomal system)<br />

•Negative (rat liver S9)<br />

Office of Environmental Health Hazard Assessment


14<br />

<strong>TNT</strong> Genotoxicity: Mammalian In Vitro Systems<br />

• Rat<br />

—Negative: in vitro liver UDS assay<br />

• Mouse<br />

—Positive: P388 lymphoma TK locus mutation<br />

assay (-S9)<br />

• Hamster<br />

—Positive: CHO-HPRT mutation assay (+S9)<br />

—Negative: V79-HGPRT mutation assay<br />

Office of Environmental Health Hazard Assessment


15<br />

<strong>TNT</strong> Genotoxicity: Mammalian In Vivo Systems<br />

• Rat<br />

—Negative: liver UDS assay<br />

—Negative: bone marrow cytogenetic damage<br />

—Positive: oxidative DNA damage (8-oxodG) in<br />

sperm cells<br />

• Mouse<br />

—Negative: bone marrow micronucleus assay<br />

Office of Environmental Health Hazard Assessment


16<br />

<strong>TNT</strong> Genotoxicity in Humans<br />

• No difference between <strong>TNT</strong>-exposed and control<br />

workers in frequency of chromosomal aberrations<br />

(CA) in peripheral blood lymphocytes<br />

� Among <strong>TNT</strong>-exposed workers<br />

—Increased CA in NAT1 rapid vs. slow acetylator<br />

genotype<br />

� Among <strong>TNT</strong>-exposed workers with NAT1 rapid<br />

acetylator genotypes<br />

—Increased CA associated with GSTM1 null or<br />

GSTT1 null genotypes<br />

Office of Environmental Health Hazard Assessment


17<br />

Genotoxicity of <strong>TNT</strong> Metabolites<br />

2-ADNT 4-ADNT 2,4-DANT 2,6-DANT<br />

Salmonella mutation<br />

assays (TA 98, TA100) + + + +<br />

CHO-HPRT<br />

mutation assay<br />

V79-HGPRT<br />

mutation assay<br />

4-NHOH-DNT<br />

- + (S9) - + (weak)<br />

- + (weak) - -<br />

- Positive: in vitro oxidative DNA damage (8-oxodG);<br />

cleaves DNA at sites with consecutive guanines<br />

Office of Environmental Health Hazard Assessment


18<br />

Urine Mutagenicity<br />

• Rats treated with <strong>TNT</strong><br />

—Positive in Salmonella<br />

• Humans exposed to <strong>TNT</strong><br />

—Increased mutagenicity in Salmonella of<br />

urine from exposed as compared with<br />

unexposed controls<br />

—Higher in NAT1 rapid vs. slow acetylators<br />

Office of Environmental Health Hazard Assessment


Structure-Activity Comparisons<br />

with Proposition 65 listed carcinogens<br />

19<br />

2,6-Dinitrotoluene 2,4-Dinitrotoluene 2-Nitrotoluene<br />

Rats: liver (♂) Rats: skin (♂),<br />

liver & mammary (♀)<br />

Mice: kidney (♂)<br />

Rats: mammary, liver &<br />

lung (♂), mammary & liver<br />

(♀)<br />

Mice: intestinal (♂, ♀)<br />

DNA and protein binding DNA and protein binding DNA and protein binding<br />

Office of Environmental Health Hazard Assessment<br />

<strong>TNT</strong>


20<br />

Potential Mechanisms of<br />

Carcinogenicity<br />

• Genotoxicity<br />

- Mutation<br />

- Induction of oxidative DNA damage<br />

Office of Environmental Health Hazard Assessment


21<br />

Authoritative Body Reviews<br />

• US EPA (1993)<br />

—Reviewed animal studies by Furedi et al. (1984a,b)<br />

—Did not include any human studies<br />

—Did not include several studies on metabolism, genotoxicity,<br />

biomarkers of exposure<br />

—Group C: “possible human carcinogen”<br />

• IARC (1996)<br />

—Did not include the epidemiology studies of Kilian et al. (2001),<br />

Yan et al. (2002)<br />

—Did not include animal cancer studies<br />

—Did not include several recent studies on metabolism,<br />

genotoxicity, biomarkers of exposure<br />

—Group 3: “not classifiable as to carcinogenicity in<br />

humans”<br />

Office of Environmental Health Hazard Assessment


22<br />

<strong>TNT</strong>: Summary of Evidence<br />

• Humans<br />

—Not adequately studied<br />

—Suggestion from case reports and controlled<br />

studies of liver cancer & leukemia<br />

• Animals<br />

—Rare urinary bladder tumors in female rats<br />

—Leukemias/malignant lymphomas of the spleen<br />

in female mice<br />

• Other relevant evidence<br />

—Genotoxicity of <strong>TNT</strong> & its metabolites<br />

—Structural similarity to the carcinogens<br />

2-nitrotoluene, and 2,4- and 2,6-dinitrotoluene<br />

Office of Environmental Health Hazard Assessment

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